Abstract

Air quality monitoring systems differ in composition and accuracy of observations and their temporal and spatial coverage. A monitoring system’s performance can be assessed by evaluating the accuracy of the emission sources identified by its data. In the considered inverse modeling approach, a source identification problem is transformed to a quasi-linear operator equation with the sensitivity operator. The sensitivity operator is composed of the sensitivity functions evaluated on the adjoint ensemble members. The members correspond to the measurement data element aggregates. Such ensemble construction allows working in a unified way with heterogeneous measurement data in a single-operator equation. The quasi-linear structure of the resulting operator equation allows both solving and predicting solutions of the inverse problem. Numerical experiments for the Baikal region scenario were carried out to compare different types of inverse problem solution accuracy estimates. In the considered scenario, the projection to the orthogonal complement of the sensitivity operator’s kernel allowed predicting the source identification results with the best accuracy compared to the other estimate types. Our contribution is the development and testing of a sensitivity-operator-based set of tools for analyzing heterogeneous air quality monitoring systems. We propose them for assessing and optimizing observational systems and experiments.

Highlights

  • Atmospheric air quality monitoring systems vary in their temporal and spatial coverage, the composition of the chemicals observed, and the accuracy of the data obtained

  • To evaluate the synergistic effect of using different measurement types, we compare the source identification results obtained for composite measurements with those obtained for the specialized measurement types

  • An essential advantage of the sensitivity-operator-based approach to inverse modeling is that various problems can be reduced in a unified way to a family of quasi-linear operator equations

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Summary

Introduction

Atmospheric air quality monitoring systems vary in their temporal and spatial coverage, the composition of the chemicals observed, and the accuracy of the data obtained. New measurement systems are deployed to obtain new air-quality data, and new observational experiments are carried out. Choosing or optimizing the configuration of a monitoring system or observational experiment [3,4,5,6,7,8,9,10,11] is a multi-criteria decision-making task. An essential criterion for choosing the configuration of the monitoring system is the value of the information content of prospective measurements. To choose one of the options, one can, for example, use the Multiple Criteria Decision-Making methods (see, e.g., [15])

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